Garden Birds. Mike Toms
between food provision and Blackcap wintering behaviour. Examination of the foods provided in Garden BirdWatch gardens and their use by wintering Blackcaps revealed a strong preference by the birds for sunflower hearts and fat-based products. By calculating an annual measure of the proportion of winter weeks in which these foodstuffs were provided at each of 3,806 sites – each of which had a minimum of at least 16 weekly submissions in a minimum of at least nine winters – it has been possible to explore the relationship between Blackcap occurrence and food provision and how this has changed over time.
Wintering Blackcaps showed regional variation in their use of Garden BirdWatch gardens, with greater occupancy of sites in the south and west (see Figure 43), where wintering conditions are milder. Occupancy rates were influenced by both the provision of supplementary food and winter temperature. Birds were recorded more often in gardens that provided food more frequently, and showed a preference for sites that had a warmer local climate during the winter months. One of the most interesting findings was that Blackcap occurrence has become more strongly associated with the provision of fat products and sunflower hearts over time, suggesting that the birds are adapting their feeding habits to exploit human-provisioned foods. This supports the theory of Berthold & Terrill (1988) that the Blackcap’s new migration strategy is likely to have evolved in response to increased supplementary feeding activities in gardens in Britain.
The results of the Plummer study also reveal that gardens are used less during milder winters, which – together with the relationship found with local climate – supports the hypothesis that an improving winter climate is likely to have enabled the Blackcap to increase its wintering range into Britain. In addition, the growing use of provisioned food adds further support to the work of Rolshausen et al. (2009), who have found that Blackcaps wintering in Britain have relatively narrower and longer beaks than those wintering in Spain. Such differences suggest that these British migrants have adapted to a more generalist diet than their Spanish counterparts, adding phenotypical divergence to the genetic divergence already documented between these two populations (Berthold et al., 1992). Rolshausen et al. also found differences in wing morphology, bill colour and plumage colour between the two populations.
WATER AND GARDEN BIRDS
Garden birds require water, both to drink and in many cases for bathing – though see Chapter 5. This water may be present in the form of a pond, puddle or bird bath and all can be well used by visiting birds. Figures from national studies suggest that 10 per cent of UK dwellings have a pond associated with them, though not all of these will be suitable for birds. Some may be netted to protect precious fish, while others may be steep-sided and inaccessible. Those with a shallow end or with branches that dip into the water are likely to be used most often, the birds able to perch within or close to the water when drinking or bathing. Just over half of the respondents to a questionnaire survey carried out by Cowie & Hinsley (1988a) in suburban Cardiff reported providing water for visiting birds. The provision of water can influence the community of birds using a garden, with seed-eating species seemingly preferring sites at which they can both feed and drink. Water may also shape behaviour – for example, by providing some garden Blackbirds with the opportunity to develop the habit of catching and eating small newts and the tadpoles of Common Frog Rana temporaria – and play a role in disease transmission. Despite this, its importance has received little research interest and there is the potential here for much new information to be gained.
FIG 44. Water is important for garden birds and the presence of a pond or other water source can prove very attractive to visiting birds. (Jill Pakenham)
GARDEN BIRD FOOD AND OTHER WILDLIFE
The food available at garden feeding stations isn’t just used by garden birds; it may be taken by other creatures or, in some instances, germinate and lead to the establishment of non-native flora. Many of the other beneficiaries of garden feeding are mammals, with mice, voles, rats and squirrels the most commonly reported feeders here in the UK. While some of these creatures are tolerated, or even encouraged, some are viewed as a pest. Common Rat Rattus norvegicus and Grey Squirrel are the two most commonly seen as a negative consequence of garden feeding. The presence of Grey Squirrels at a garden feeding station may prevent birds from taking food, something determined experimentally by Hugh Hanmer and colleagues at the University of Reading (Hanmer et al., 2018).
FIG 45. Some garden feeding station visitors are less welcome than others. (John Harding)
Efforts to deter squirrels from garden feeding stations tend to be based around either the physical adaptation of feeding devices or treatment of the food itself. Two other options – providing squirrels with their own feeder some distance from the feeding stations, and lethal control – are not widely practised. Treatment of peanuts and other foods with capsaicin – the pungent component that is responsible for the sensation one gets when eating chilli peppers – has proved a useful deterrent in trials carried out in the US (Curtis et al., 2000). Treatment of sunflower seeds significantly reduced both the amount of seed taken by Grey Squirrels and the amount of time that they spent feeding, but did not affect the amount of seed taken by feeding birds. Capsaicin binds to pain receptors in mammals and has a number of other effects that result in many mammals finding the substance repellent. Although at least some bird species can taste capsaicin, it does not appear to be harmful or repellent to them. There is, however, one other finding worth mentioning here, which is that Grey Squirrels can learn to open treated sunflower seeds, avoiding the treated husk to feed on the heart (Fitzgerald et al., 1995). Fortunately, a company in the US has developed a way to treat both the husk and the heart within.
A perhaps unforeseen consequence for wider biodiversity on the provision of food at garden feeding stations is that the presence of increased numbers of insectivorous or omnivorous birds can lead to increased levels of predation of garden-dwelling invertebrates. Investigating the possible effects of wild bird feeding on the size and survivorship of Pea Aphid Acyrthosiphon psium colonies in suburban gardens, Melanie Orros and Mark Fellowes found that the presence of bird feeders had a significant impact. Both the size and survivorship of aphid colonies was significantly reduced in gardens where a feeding station was present (Orros & Fellowes, 2012). The same researchers have also found that supplementary feeding of garden birds indirectly affects ground beetle populations (Orros et al., 2015a), and work in the US suggests a similar impact on arthropods overwintering on bark (Martinson & Flaspohler, 2003).
CONCLUDING REMARKS
A key take-home message about bird feeding is that there is still a lot for us to learn; it is no longer appropriate to merely follow the simplistic view that feeding garden birds is largely beneficial, and that any deleterious aspects are outweighed by the benefits gained. Some authors have even suggested that bird feeders are ecological traps, perhaps tempting birds to initiate breeding attempts earlier in the year than is beneficial and leading to a mismatch between the food demands of the resulting chicks and the availability of the peak invertebrate resources on which they depend. The scrub-jays breeding in suburban habitats with access to supplementary food may well breed earlier but they can find themselves out of synch with the natural food items that they need for their growing nestlings, something that could potentially lead to decreased rather than increased breeding success (Schoech & Bowman, 2001).
The provision of supplementary foods, many of which would not be taken by these species within the wider environment, has complex effects on individual birds and their broader populations. The extent to which food provision is considered to be deleterious or beneficial will, in part, depend on whether you are examining its effects at the level of the individual bird or the wider population. Feeding can change the structure of populations, something that may have profound consequences for the size of broader populations, both of the species under study and, potentially, those of the other species with which it competes or interacts. The effects of supplementary food may also differ depending upon external factors, perhaps having the greatest impact when times are tough or in